2,4-D Mineralization as Affected by Pre-Incubation Length of Amended Soils
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2,4-D Mineralization as Affected by Pre-Incubation Length of Amended Soils
2,4-D Mineralization as Affected by Pre-Incubation Length of Amended Soils M. Reimer and A. Farenhorst; Department of Soil Science, University of Manitoba, Winnipeg, MB, Canada Introduction Objective Conclusions Since its introduction in the 1940’s, 2,4-D (2,4dichlorophenoxyacetic acid) has been a widely used broadleaf herbicide. Soil microbes play a large role in the degradation and mineralization of 2,4-D in soil. The addition of organic amendments, such as livestock manure or municipal biosolids, can affect the organic matter content, microbial population and nutrient status of soil. These properties of organic amendments may play an important part in determining the fate of 2,4-D in soil. The objective of this study was to determine whether increasing the amount of time between applications of fresh hog manure or municipal biosolids and 2,4-D application would result in a change in the total mineralization of 2,4-D. Longer incubation time decreased the total amount of 2,4-D mineralization. Applying 2,4-D immediately following amendment addition results in the greatest total 2,4-D mineralization. 28 days of amendment pre-incubation resulted in the lowest total mineralization. This data has implications for producers who apply amendments and pesticides within a narrow time frame. There may be less risk of 2,4-D carryover and possible crop damage when 2,4-D is applied immediately after amendment application. Figure 1. 2,4-D Molecule Cl Results For both amendment treatments and the control soil, total 2,4-D mineralization decreased with increasing pre-incubation time (Figure 3). Differences were greatest for the biosolid-amended soils, where the total herbicide mineralization decreased from 47% (2,4-D immediately applied) to 21% (2,4-D applied at 28 days following amendment application). For manure-amended soil, total herbicide mineralization decreased from 42% to 20%, while the differences in mineralization were much smaller for the control soil. The soil was incubated at 20oC for 0, 7, 14, or 28 days prior to addition of 2,4-D, which was applied at a rate of 0.62 kg active ingredient/ha as a mixture of For applications of 2,4-D immediately following amendment additions (Figure 3; 0 days), greatest total 2,4-D mineralization was measured in biosolid-amended soils, intermediate in manured soils, and lowest in control soils. radio-labelled and analytical grade 2,4-D. Small vials containing 5 mL of 0.5M NaOH were used to trap the 14CO as it evolved from the soil and 2 measured using liquid scintillation counting. Mineralization was measured for 100 days after 2,4-D addition and quantified as the amount of 14CO2 evolved from the soil as a percen-tage of the initial 14C 2,4-D applied. Figure 2. Soil microcosm For more information, contact: [email protected] These differences were not as pronounced when 2,4-D was added 7, 14 or 28 days after amendment application. Mineralization was greater in the biosolid-amended soil in the 7-day pre-incubation treatment than in manured or control soils, but similar total mineralization was measured in the biosolid- and manure-amended soils in the 14 and 28-day pre-incubation lengths. 50 45 40 35 30 25 20 15 10 5 0 Manure 0 Days 7 Days 14 Days Biosolid Control 28 Days Figure 3. 2,4-D Mineralization in amended soils preincubated for different lengths of time The control soil reached greater total 2,4-D mineralization in the 14-day pre-incubation treatment than in amended soils, and reached similar total mineralization in the 28-day treatment as the amended soils. In fact, there is no significant effect of incubation length on 2,4-D total mineralization in control soils. 255 2,4-D mineralization was measured in a Chernozemic sandy loam soil collected near Macgregor, MB. Samples from the top 10 cm of the soil profile were passed through a 2 mm sieve. Microcosms were assembled using 500 ml mason jars (Figure 2). 30 g of soil was placed in a small jar, to which 112 kg N/ha (as NH4+-N) of fresh hog manure and municipal biosolids were added, or left untreated (control). Moisture content of the soil was brought up to 70% field capacity. % Mineralization Methods and Materials OCH2COOH Cl